Fen Management Handbook - Scottish Natural Heritage
Fen Management Handbook - Scottish Natural Heritage
Fen Management Handbook - Scottish Natural Heritage
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10.3.3 Vegetation Mapping<br />
An initial identification of the plant communities present in a fen, with approximate<br />
mapping of the community boundaries, is crucial for identification of key species<br />
and informing the understanding of physical mechanisms affecting a site. This is<br />
usually based on a survey using the NVC methodology (Rodwell J. S. ed. 1991 –<br />
2000).<br />
The NVC methodology is both rigorous (i.e. careful application of the method will<br />
yield consistent and reliable results) and robust (i.e. it is not sensitive to minor<br />
differences in technique). However, it is a plant community classification method,<br />
not a mapping or monitoring method. The recording method is based on selecting<br />
locations for quadrats that appear typical of the community that is being observed,<br />
well within the boundaries of that apparent community.<br />
A set of NVC quadrats can provide an almost complete species list for a defined<br />
area, which can be quickly completed by a check for other species outside the<br />
quadrats, using the DAFOR abundance scale. This can provide the basis for the<br />
qualitative monitoring of the community in that part of the site.<br />
Basic fen monitoring techniques<br />
Quadrats are square frames (usually 4 square metre (2x2m) on fens)<br />
used to sample vegetation. The presence of plant and moss species and<br />
their relative density or abundance is recorded within the quadrat. The<br />
location of the quadrat is described with a GPS, or marked with a post,<br />
so that the vegetation can be re-surveyed and described repeatedly at<br />
the same location in future to detect changes. Further information on<br />
quadrat methodology can be found in Ecological Census Techniques<br />
(Sutherland, 2006).<br />
Transects, or lines, are used to sample vegetation along a gradient<br />
or gradual change of the vegetation. The transect can be up to 100<br />
m long or more, the length depending on the changes or gradient to<br />
be monitored. Vegetation is normally sampled with a quadrat at fixed<br />
intervals, say every 5 m, along the transect, or where tall vegetation (such<br />
as reed encroachment) or abiotic changes (such as change in slope,<br />
groundwater seepage zone) occur. The environment is also normally<br />
measured along the same transect so that changes in vegetation can be<br />
correlated to changes in the environment, and vice-versa.<br />
Advantages of vegetation community mapping and survey include:<br />
– The NVC methodology can provide a clear and rigorous description of the plant<br />
communities present on the site.<br />
– A set of well recorded NVC quadrats can provide useful species presence and<br />
abundance data for a defined location.<br />
– Where well-defined, boundaries between communities can be accurately mapped<br />
using appropriate techniques.<br />
– Two sets of data are generated; geographical data for the community extent and<br />
qualitative data for the community composition in a particular area of the site.<br />
– The data can be presented graphically, as readily comprehensible maps.<br />
– GIS mapping gives precise measurement of areas, allowing changes to be quantified.<br />
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